Octan-1-ol

Short-term toxicity to fish

Link to relevant study record(s)

Reference

Endpoint:

short-term toxicity to fish

Type of information:

experimental study

Adequacy of study:

key study

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

comparable to guideline study with acceptable restrictions

Remarks:

Study conducted according to sound scientific principles in accordance with GLP. Analytical monitoring was performed however no details of analysis were provided. Insufficient details to assign a higher reliability to the study.

Qualifier:

according to guideline

Guideline:

other: ASTM 1980

Deviations:

not specified

Qualifier:

equivalent or similar to guideline

Guideline:

OECD Guideline 203 (Fish, Acute Toxicity Test)

Deviations:

not applicable

GLP compliance:

yes

Analytical monitoring:

yes

Details on sampling:

- Concentrations: all concentrations

- Sampling method: one sample from each test chamber, daily.

Vehicle:

not specified

Details on test solutions:

PREPARATION AND APPLICATION OF TEST SOLUTION

- Method: Benoit et al. (1982) and Anderson & Weber (1975)

Test organisms (species):

Pimephales promelas

Details on test organisms:

TEST ORGANISM

- Common name: fathead minnow

- Source: US EPA Environmental Research Laboratory-Duluth

- Age at study initiation (mean): Newly hatched fry were < 24 hours old and juvenile fathead minnows 28 to 34 days old

- Weight at study initiation (mean): 0.12 g

- Feeding during test: none


ACCLIMATION

- Acclimation period: 2-3 hours prior to test initiation.

- Acclimation conditions: same as test

- Type and amount of food: fresh hatched brine shrimp nauplii and dry flake Tetramin during their first week

- Feeding frequency: shrimp 2-3 times a day until 24h before the test

- Health during acclimation: good

Test type:

flow-through

Water media type:

freshwater

Limit test:

no

Total exposure duration:

96 h

Post exposure observation period:

none

Hardness:

average: 44.6 ± 1.4 mg/L as CaCO3

Test temperature:

25 ± 1 ºC

pH:

average: 7.6 ± 0.2

Dissolved oxygen:

>80%

Salinity:

N.A.

Nominal and measured concentrations:

Four treatment levels and a control.

Details on test conditions:

TEST SYSTEM

- Test vessel: chambers with silicone sealant

- Type: closed

- Material, size, headspace, fill volume: glass, filled with 2L of test solution

- Aeration: in head water reservoirs

- Type of flow-through: proportional diluter.

- Renewal rate of test solution: water replacement 2-4 h (25 ml/min), 95% replacement in 4 h.

- No. of organisms per vessel: 5

- No. of vessels per concentration: 1

- No. of vessels per control: 2



TEST MEDIUM / WATER PARAMETERS

- Source/preparation of dilution water: filtered Lake Superior water

- Alkalinity: 44.0 mg/l as CaCO3


OTHER TEST CONDITIONS

- Adjustment of pH: none reported

- Photoperiod: 16 h daylight

- Light intensity: 22 to 38 lumens/sq ft


EFFECT PARAMETERS MEASURED: mortality, measured daily.


TEST CONCENTRATIONS

- Spacing factor for test concentrations: 0.8

Reference substance (positive control):

not specified

Key result

Duration:

96 h

Dose descriptor:

LC50

Effect conc.:

13.3 mg/L

Nominal / measured:

meas. (not specified)

Conc. based on:

not specified

Basis for effect:

mortality (fish)

Remarks on result:

other: fry fish

Key result

Duration:

96 h

Dose descriptor:

LC50

Effect conc.:

13.5 mg/L

Nominal / measured:

meas. (not specified)

Conc. based on:

not specified

Basis for effect:

mortality (fish)

Remarks on result:

other: juvenile fish

Details on results:

- Mortality of control: No control mortality in tests with juveniles and less than 10% in tests with fry (refers to all 27 chemicals tested in study)

Reported statistics and error estimates:

LC50 and 95% confidence intervals were computed by the Trimmed Spearman-Karber Method (Hamilton et al. 1977) or a log-probit method (Stephan 1977).

Validity criteria fulfilled:

not specified

Conclusions:

96h LC50 values of 13.3 and 13.5 mg/L were determined for the effects of the test substance on the mortality of fry and juvenile Pimephales promelas respectively.

Description of key information

Short-term toxicity to fish: 96 h LC₅₀: 13.3 mg/l (measured concentration) for the effects of the test substance on mortality of fry Pimephales promelas (guideline ASTM 1980).

Key value for chemical safety assessment

Fresh water fish

Fresh water fish

Effect concentration:

13.3 mg/L

Additional information

A reliable 96 h LC₅₀ value of 13.3 mg/L has been determined for the effects of octan-1-ol (CAS 111-87-5) on mortality of the fish Pimephales promelas (Broderius & Kahl, 1985). This study represents the lowest reliable value available for this endpoint on octan-1-ol.

This result is supported by consistent literature values in several freshwater fish species and is also consistent with QSAR predictions.

Reliable supporting short term toxicity to fish tests and estimates have determined the LC₅₀ to lie in the range of 15 to 20 mg/L. A NOEC of 1.5 mg/l has been determined in a prolonged fish toxicity test:

48 h LC₅₀ Leuciscus idus = 20 mg/l (Reliability 4) [Juhnke I, Luedemann D, 1978].

96-h LC₅₀ Alburnus alburnus (brackish water species) = 16 mg/L (reliability 4) [Bengtsson B et al, 1984; Linden E et al, 1979].

48 h LC₅₀ Leuciscus idus = 16 mg/l (Reliability 4) [Juhnke I, Luedemann D, 1978].

96-h LC₅₀ (no species named) = 18 mg/l (reliability 2) [Huntingdon Life Sciences Ltd, 1996].

48-h LC₅₀ Leuciscus idus = 17 mg/l (reliability 2) [Henkel KGaA, 1999].

96-h LC₅₀ fish taxonomic group = 15 mg/l (QSAR, reliability 2) [Fisk PA, 2009].

7-d NOEC Pimephales promelas = 1.5 mg/l (reliability 2) [Pickering Q H, Lazorchak J M, Winks K L, 1996].

96-h LC₅₀ Salmo gairdneri (new name: Oncorhynchus mykiss) = 17.7 mg/l [McKim J M et al., 1987].

Discussion of trends in the Category of C6-24 linear and essentially-linear aliphatic alcohols:

Linear LCAAs

The data summarised in the table below show that the toxicity of the single carbon number chain length LCAAs increases from an LC₅₀ of 97 mg/L for C6 to 1.0 mg/L for C12. At higher carbon number chain lengths there is an absence of short-term toxicity (LC₅₀ values are reported as being greater than the highest test concentration or higher than the water solubility of the test substance) and this is explained by the water solubility of an LCAA limiting its bioavailability, such that a toxic concentration for short-term exposure is not achieved.

The results of a 7-day, semi-static toxicity test with 1-octanol using Pimephales promelas larvae aged 1, 4 and 7 days at the start of the study have also been reported by (Pickering et al., 1996) but are not included in the table. NOECs based on nominal concentrations were 1.5-11.9 mg/L for survival. Measured concentrations in the test were reduced to non-detectable levels in most test vessels in the old media. The poor maintenance of exposure concentrations means that the reported NOEC values are almost certainly underestimates of the true toxicity of the substance. The results of this test are also discussed later with respect to long-term toxicity.

The lowest reliable LC₅₀ values determined in tests with single carbon chain length LCAAs are shown in the following table. 

Table: Key fish short-term toxicity studies on single carbon chain length linear LCAAs.

CAS	Chemical Name	Comments	Water solubility (mg/L)	Species	Method/ Guideline	Exposure regime	Endpoint	Value (mg/L)^1,2	Reliability code	Reference
111-27-3	1-Hexanol		5900 at 20°C	Pimephales promelas	US EPA 1975	Flow-through	96 h LC50	97 (m)	2	Veith, Call and Brooke, 1983a,b
111-70-6	1-Heptanol	Supporting	1300 at 20°C	Pimephales promelas	ASTM 1980	Flow-through	96 h LC50	38 (m)	2	Broderius and Kahl, 1985
111-87-5	1-Octanol		550 at 25°C	Pimephales promelas	ASTM 1980	Flow-through	96 h LC50	13 (m)	2	Veith, Call and Brooke, 1983a,b; University of Wisconsin-Superior., 1984; Broderius and Kahl, 1985
143-08-8	1-Nonanol		130 at 20 °C	Pimephales promelas	ASTM 1980	Flow-through	96 h LC50	5.5 (m)	2	Broderius and Kahl, 1985
112-30-1	1-Decanol		40	Pimephales promelas (embryo)	OECD TG 236	Flow-through	120 h LC50	3.4 (m)	1	Wildlife International, 2015b
112-30-1	1-Decanol		40	Pimephales promelas	US EPA 1975	Flow-through	96 h LC50	2.3 (m)	2	Veith, Call and Brooke, 1983a,b; Brooke et al., 1984
112-42-5	1-Undecanol		8.0 at 20°C	Pimephales promelas	US EPA 1975	Flow-through	96 h LC50	1.0 (m)	2	Veith, Call and Brooke, 1983a,b
112-53-8	1-Dodecanol		1.9 at 20°C	Pimephales promelas	US EPA 1975	Flow-through	96 h LC50	1.0 (m)	2	Veith, Call and Brooke, 1983a,b
112-70-9	1-Tridecanol	Supporting	0.38 at 20°C	Pimephales promelas	US EPA 1975	Flow-through	96 h LC50	>0.33 (m)	2	Veith, Call and Brooke, 1983a,b
112-72-1	1-Tetradecanol		0.19 at 25°C	Salmo gairdneri i^3	OECD 203	Semi-static	96 h LC50	>1 (n) (>LoS)	2	SafePharm, 1996b
36653-82-4	1-Hexadecanol		0.013 at 25°C	Salmo gairdneri^3	OECD 203	Semi-static	96 h LC50	>0.4 (n) (>LoS)	2	SafePharm, 1996c
112-92-5	1-Octadecanol		0.0011 at 25°C	Salmo gairdneri^3	OECD 203	Semi-static	96 h LC50	>0.4 (n) (>LoS)	2	SafePharm, 1996d
661-19-8	1-Docosanol		approx. 0.001 (estimate)	Oncorhynchus mykiss	OECD 203	Semi-static	96 h LC50	>1000 (n) (>LoS)	2	SafePharm, 2000

Notes:

1 >LoS: concentration/Loading rate greater than the limit of water solubility

2 (n) based on nominal concentrations, (m) based on measured concentrations.

3 Now known as Oncorhynchus mykiss. The names used in the study reports are given here.

 

Multi-constituent LCAAs

The data for multi-constituent substances of different carbon chain length LCAAs (commercial products) are shown in the table below. The results show that substances containing LCAAs with carbon numbers in the ranges of C8-10 and C6-12 exert short-term toxic effects at concentrations of between 0.7 and 10 mg/L. At these concentrations, all the constituents are likely to have been fully dissolved.

In contrast, multi-constituent substances - Alcohols, C12-13; Alcohols, C12-13-branched and linear and Alcohols, C12-15-branched and linear - exhibited effects at loading rates where not all constituents were fully dissolved. Under such circumstances the presence of retained undissolved test material, such as occurred in the Shell Toxicology Laboratory (1978a) test, opens up the possibility for physical fouling of the test organism and this needs to be kept in mind when interpreting the result. The multi-constituent substances containing LCAAs with carbon chain length C12 and above did not exhibit short-term toxicity effects at loading rates where the solubility of the constituent LCAAs was exceeded.

The data for nonanol, branched and linear, decanol branched and linear, decanol branched and undecanol branched alcohols, have been read-across from their linear alcohols counterparts (C9, C10 and C11) since they are essentially linear alcohols.

Alcohols, C14-15 ecotoxicity assessment is based on weight of evidence from two studies; Shell Internationale Chemie (1973) and Shell Toxicology Lab (1978a). Both studies report the LC₅₀ to be above the limit of solubility. The Shell Internationale Chemie (1973) study tested the toxicity of the substance via the WAF preparation method (the preferred method of testing with poorly soluble mixtures) however it does not report complete information on the study methods and conditions. The Shell Toxicology Lab (1978a) did not utilise WAF methods but it is reported more comprehensively.

The results for both single carbon number LCAAs and the multi-constituent substances indicate that, for fish, there is a short-term toxicity cut-off for LCAAs with carbon numbers >C14.

 

The lowest reliable LC₅₀ values determined in tests with multiconstituent carbon chain length LCAAs are shown in the following table.

Table: Fish short-term toxicity studies on mixed carbon chain length LCAAs.

CAS #	Chemical name	Comments^1	Water solubility (mg/L)	Species	Method/ Guideline^2	Exposure regime	Endpoint	Value (mg/L)^3	Reliability code	Reference
n/a	Alcohols, C7-9	SUPPORTING	510 at a loading rate of 1000 mg/L (estimated)	I. idus^4	Not specified	Static	96 h LC50	0.7-0.8 (n)	4 (disregarded)	Shell, 1978
67762-41-8	Alcohols, C8-10	Type C SUPPORTING	2.4 at 25°C	Salmo gairdneri^4 and Lepomis macrochirus	EPA 1975	Static	96 h LC50	6.5-10 (n)	2	EG&G Bionomics, 1975
66455-17-2	Alcohols, C9-11	SUPPORTING	44 at a loading rate of 1000 mg/L. (estimated)	S. gairdneri^4	Not specified	Static	96 h LC50	6.3-10 (n)	2	Shell Toxicology Laboratory, 1979
66455-17-2	Alcohols, C9-11	SUPPORTING	44 at a loading rate of 1000 mg/L. (estimated)	Scopthalmus maximus (marine species)	Not specified	Semi-static	96 h LC50	5.8 (n)	2	Huntingdon Life Sciences Ltd., 1991d
68515-81-1	Nonanol, branched and linear		121 (estimated)	Pimephales promelas	ASTM 1980	Flow-through	96 h LC50	5.5 (m)   (r-a from C9)	2	Broderius and Kahl, 1985
90342-32-8	Decanol, branched and linear		26.17 at 20°C	P. promelas	US EPA 1975	Flow-through	96 h LC50	2.3 (m)   (r-a from C10)	2	Veith, Call and Brooke, 1983a,b; University of Wisconsin-Superior, 1984
128973-77-3	Undecanol, branched and linear. Reaction mass of 2-methyldecan-1-ol and 2-propyloctan-1-ol and 2-ethylnonan-1-ol and 2-butylheptan-1-ol		6.3 at 25°C	P. promelas	US EPA 1975	Flow-through	96 h LC50	1.0 (m) (r-a from C11)	2	Veith, Call and Brooke, 1983a,b
75782-86-4	Alcohols, C12-13		2.4 at 25^oC	S. gairdneri^4	Not specified	Static	96 h LC50	4.0-10 (>LoS)	2	Shell Toxicology Laboratory, 1978a
75782-86-4	Alcohols, C12-13		2.4 at 25^oC	S. maximus (marine species)	Not specified	Semi-static	96 h LC50	10 (n) (>LoS)	2	Huntingdon Life Sciences Ltd., 1991c
740817-83-8	Alcohols, C12-13-branched and linear		2.9-3.1 at 20°C	Brachydanio rerio	OECD 203 WAF	Semi-static	96-hr LL50	15 (n) (>LoS)	1	TNO, 2000a
90604-40-3	Alcohols, C12-15-branched and linear		0.80 at 20°C	Oncorhynchus mykiss	OECD 203 WAF	Semi-Static	96 h LL50	100-300 (n) (>LoS)	1	Shell Global Solutions, 2000
68855-56-1	Alcohols, C 12-16	Type B SUPPORTING	0.80 at 20°C	O. mykiss	Not specified	Static	96 h LC50	57 (n) (>LoS)	2	Huntingdon Life Sciences 1996i
80206-82-2	Alcohols, C 12-14	not possible to determine compositional type SUPPORTING	approx. 4 predicted at 1000 mg/L loading rate	L. idus	OECD 203	Static	48 h LC50	>5000 (n) (>LoS)	2	Henkel, 1999m
75782-87-5	Alcohols, C14-15		0.7 at 20°C and 0.15 at a loading rate of 1000 mg/L. (estimated)	S. gairdneri4	Not specified	Static	96 h LL50	>500 (n) (>LoS)	2	Shell Toxicology Lab 1978b
75782-87-5	Alcohols, C14-15		0.7 at 20°C and 0.15 at a loading rate of 1000 mg/L. (estimated)	Carassius auratus	Not specified	Static	96 h LL50	>0.7 (n) (>LoS)	2	Shell Internationale Chemie, 1973
68002-94-8	Alcohols, C 16-18 and 18 Unsaturated	SUPPORTING	0.0404 predicted at 1000 mg/L loading rate	L. idus	OECD 203	Static	48 h LC50	>10000 (>LoS)	2	Henkel, 1999o

Notes:

1  Compositional Types are described in section 1.5 of the ecotoxicity category report.

2  WAF denotes test medium was a water-accommodated fraction      

3  >LoS: LC₅₀  observed was greater than the limit of solubility of at least some constituents of the substance. (n)  based on nominal concentrations,  (m) based on measured concentrations.

4  Now known as  Oncorhynchus mykiss. The names used in the study reports are given here.

 

References:

Broderius, S. and Kahl, M., 1985. Acute toxicity of organic chemical mixtures to the fathead minnow. Aquatic Toxicology 6:307-322.

E.G.& G. Bionomics, 1975. Acute toxicity of two Conoco compounds to bluegill (lepomis macrochirus) and rainbow trout (Salmo gairdneri). Bioassay report submitted to Conoco Chemicals, Ponca City, Oklahoma.

Henkel KGaA, 1999m. Biological research and Product Safety/Ecology: Unpublished results; test substance registration No. 6801.

Henkel KGaA, 1999o. Biological Research and Product safety/Ecology: unpublished results, test substance registration no. 6802.

Huntingdon Life Sciences Ltd. (HLS), 1991d. Report No. SLL 207(d)/911034.

Huntingdon Life Sciences Ltd. (HLS), 1991c. Report No. SLL 207(c)/911033.

Huntingdon Life Sciences Ltd. (HLS), 1996i. Report No. 96/KAS231/0417.

SafePharm Laboratories, 1996b. SafePharm Laboratories SPL Project Number 140/599.

SafePharm Laboratories, 1996c. SafePharm Laboratories SPL Project Number 140/500.

SafePharm Laboratories, 1996d. SafePharm Laboratories SPL Project Number 140/506.

SafePharm Laboratories, 2000. SafePharm Laboratories SPL Project Number 140/1001.

Shell, 1978. The acute toxicity of Linevol 79 to the golden orfe (idus idus melanotus), Shell Group Research Report, TLGR.0024.78.

Shell Global Solutions, 2000. Shell Global Solutions Report CT.99.47088.

Shell Internationale Chemie, 1973. Determination of acute toxicity to fish of Shell chemicals. I. AMGR.0095.73. Shell Toxicology Laboratory, 1978a. GRR-TLGR.0161.78.

Shell Toxicology Laboratory, 1978b. GRR-TLGR.0162.78.

Shell Toxicology Laboratory, 1979. GRR-TLGR.0166.78.

TNO Nutrition and Food Research Institute, 2000a. Semi-static acute toxicity test with Compound 33A and the zebra fish Brachydanio rerio. TNO report V98.1319. University of Wisconsin-Superior, 1984. Acute Toxicities of Organic Chemicals to Fathead Minnows (Pimephales promelas). Center for Lake Superior Environmental Studies, University of Wisconsin-Superior.

Veith, G.D., Call, D.J., and Brooke, L.T., 1983a. Estimating the acute toxicity of narcotic chemicals to fathead minnows. In: Bishop, W.E., Cardwell, R.D., and Heidolph, B.B. (eds.). Aquatic Toxicology and Hazard Assessment: Sixth Symposium. ASTM STP 802. American Society for Testing and Materials, Philadelphia.

Veith, G.D., Call, D.J., and Brooke, L.T., 1983b. Structure-toxicity relationships for the fathead minnow, Pimephales promelas: Narcotic industrial chemicals. Can. J. Fish. Aquat. Sci. 40:743-748.

Wildlife International, 2015b. Decanol: A static-renewal fish embryo acute toxicity (FET) test with the fathead minnow (Pimephales promelas) Final Report; Wildlife International Project Number: 774A-101; OECD Guideline 236.